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� "' c ���-.��.�•r�.. €�,y_.�3 -���°"._:F ��,�,� �-'�,rn*�.."`�.. '�'� '�t� F �� � �' "a'.-xs 9. :��- �.m ��Y:x'�f��' �.�.e� �." �i <br /> :. �� -u., � r.-_. .r.F�:.zZr� :. ��«'r`.`'s+',. .ate 4.'�.s'.k,% .=�-a ;.-..Sk�•. ''. ~ ?•�.�L�: � 3-.-,'Yt,.;�n. �:" �.�,ssi �, �"t�-.'t��`3I"i ��� e' � -e�s':�� �'� <br /> z <br /> - I <br /> the, relatively dense soil, the local implementing Agency inspector dacides <br /> not to have the interface soil sampled and han the bnckhoe dig deeper 10 sg:a <br /> If the contnminntion diminishes to acceptable levels. This exploration nnvrn <br /> the property owner the cunt of running two nomplea at that location, and <br /> onabien the Inapactor to directiy observe the condition of the danpar soil. <br /> In both exrmples, different material €n collected in lieu of a standard RWQCIi <br /> interface aample. Purthar, the materinl collected in substnntinlly different <br /> from what would have boon obtained by taking representative Boil at the <br /> Board specified sampling location. Note that both of there samples were <br /> taken at the direction of the local implementing agency inspector who wan <br /> present at the site and elected to select alternative sampling locations. <br /> Note too, that these alternative samples may provide more information about <br /> the site than standard Board specified samples. However, as the LIA elected <br /> samples do not accurately reflect soil conditions at the sampling points <br /> specified by the RWQCB, the decision making process may be hampered. <br /> s <br /> Clearly there is no advantage In limiting the ability of the regulator in the <br /> field to make prudent judgements. Likewise, regulatory personnel and <br /> consultants who will review the reports without benefit of having been <br /> present at the site need to know that the samples taken were not obtained at <br /> the standard locations. A Mmpls resolution to these situations Is a brief <br /> notation indicating that the aampling was elective rather than In accordance <br /> t with a standard Board specification. Theme notations appear in the third <br /> r column or the TABLE OF SAMPLING LOCATIONS AND ANALYTICAL RESULTS. <br /> By referring to the notations in column three and four in the TABLE, any <br /> ` party reviewing the report should be able to determine if something other <br /> than Board standard samples were obtained, and when variant sampling was <br /> performed, clarify whether it was elected by the LIA inspector, elected by <br /> our field personnel, or the result of some physical condition at the site <br /> that made it impossible to obtain material from the correct sampling <br /> location. <br /> SAMPLING METHODOLOGIES USED ON THIS PROJECT <br /> �.. STANDARD RWQCH INTERFACE SAMPLE: The tank removal sampling followed the <br /> standard protocol for obtaining Interface samples. These samples fall into <br /> the category of samples which are known to be of primary concern to the <br /> Interested regulatory agencies for determining if additional action will be <br /> required at a site and the methodology has been closely defined in State and <br /> r RWQCB publications, supplements, and presentations. These specify both the <br /> acceptable depth and lateral situation of sample collection points. In <br /> accordance with these specifications, sample collection in executed as close <br /> — - <br /> an <br /> _pcoulble to the center line_{longitudinal_axisl_of_the tank_and_an_n ___ <br /> vertical axis with the fill pipe. A corresponding location Is also found at <br /> the apposite end of the leek whenever standard interface samples are being <br /> collected. <br /> Briefly, the method consists of digging up native soil from directly below <br /> the fill pipe and the corresponding opposite and of the tank and obtaining a <br /> . Sampling Report 88057-C-1 Chevron 1918 SUCTION TWO/page 8 <br /> { <br /> Al <br />